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2900 - Site Mitigation Program
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PR0505092
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Last modified
2/5/2019 4:58:08 PM
Creation date
2/5/2019 4:46:43 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0505092
PE
2960
FACILITY_ID
FA0006532
FACILITY_NAME
LYOTH LOADING STATION/CHEVRON
STREET_NUMBER
26501
Direction
S
STREET_NAME
BANTA
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
26501 S BANTA RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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GEOMgTq(x <br /> Ms. Katie Hower <br /> Chevron Pipe Line Company <br /> 19 March 1997 <br /> Page 2 <br /> distribution of the residual petroleum is above and below the current water table, probably due to <br /> historical fluctuations in the water table. This distribution of petroleum below the water table <br /> allows for a direct assessment of its potential threat to groundwater, because the presence of <br /> petroleum in contact with groundwater functionally represents a long-term in situ leaching test. <br /> Old Valley Pipeline sites are assumed to have reached chemical equilibrium or steady-state <br /> conditions because of the age of the release. <br /> INVESTIGATION/MONITORING APPROACH <br /> At each site impacted by residual petroleum from the Old Valley Pipeline, CPL will evaluate the <br /> potential threat to groundwater and, if applicable,risks to human health. Because the potential <br /> source is essentially the same between sites, a consistent approach will provide data for this <br /> evaluation. Based on the lessons learned from investigations at several Old Valley Pipeline sites, <br /> the following approach will be used, as discussed below and presented in a flow chart format <br /> (Figure 2); analytical requirements are discussed in the next section. The data requirements for <br /> each of these steps may be met by using historical site data, a new data collection program, or by a <br /> combination thereof. <br /> 1. The lateral and vertical extent of affected soil shall be defined and preliminary (or <br /> screening level) groundwater information shall be obtained using either historical or newly <br /> acquired data. A soil boring/grab groundwater sampling method is acceptable to provide <br /> this data. The petroleum-affected area must be clearly constrained. Several groundwater <br /> samples will be collected immediately downgradient of affected soil (if gradient direction <br /> is known). If gradient direction is unknown, groundwater samples will be collected from <br /> locations such that a plume would be detected (if one exists). A groundwater sample will <br /> be collected from within the affected soil area. The potential for interferences to the <br /> groundwater measurements by petroleum-affected particulates and/or biogenic byproducts <br /> will be addressed using filtering and/or silica gel cleanup steps(see following discussion). <br /> 2. If all groundwater sample results are non-detect or less than RWQCB Water Quality <br /> Objectives (WQOs), then the site will be identified as a"soil only" (vadose zone) case and <br /> the County Health Department(or equivalent) will provide regulatory oversight. Potential <br /> risks to human health posed by residual petroleum in soil will be evaluated under <br /> appropriate land use scenarios. <br /> 3. If groundwater sample results meet or exceed WQOs, the site will be identified as a <br /> "groundwater" case and the lateral and vertical extent of dissolved petroleum in <br /> groundwater will be determined using a screening method. <br /> 4. Monitoring wells will be installed as per the distribution of dissolved petroleum identified <br /> by the screening data and a quarterly monitoring program will be implemented. <br />
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